The role of arbuscular mycorrhizal fungi in the transfer of nutrients between white clover and perennial ryegrass Rogers, J. B., Laidlaw, A. S., & Christie, P. (2001). The role of arbuscular mycorrhizal fungi in the transfer of nutrients between white clover and perennial ryegrass. Chemosphere, 42, 153-159. Published in: Chemosphere Queen's University Belfast - Research Portal: Link to publication record in Queen's University Belfast Research Portal General rights Copyright for the publications made accessible via the Queen's University Belfast Research Portal is retained by the author(s) and / or other copyright owners and it is a condition of accessing these publications that users recognise and abide by the legal requirements associated with these rights. Take down policy The Research Portal is Queen's institutional repository that provides access to Queen's research output. Every effort has been made to ensure that content in the Research Portal does not infringe any person's rights, or applicable UK laws. If you discover content in the Research Portal that you believe breaches copyright or violates any law, please contact [email protected]. Download date:18. Jun. 2017 Chemosphere 42 (2001) 153±159 The role of arbuscular mycorrhizal fungi in the transfer of nutrients between white clover and perennial ryegrass Jacqueline B. Rogers a,1 , A. Scott Laidlaw a,* , Peter Christie b a b Department of Applied Plant Science, The QueenÕs University of Belfast, Newforge Lane, Belfast BT9 5PX, UK Department of Agricultural and Environmental Science, The QueenÕs University of Belfast, Newforge Lane, Belfast BT9 5PX, UK Abstract A glasshouse experiment was conducted in which 15 N was used as a tracer applied as (15 NH4 )2 SO4 to donor plants of white clover and perennial ryegrass. Nitrogen transfer via hyphae of arbuscular mycorrhizal fungi (AMF) or by other routes was studied by separating the root systems of the two plant species, as donors and receivers, when growing in the same pot, with selective mesh barriers of varying pore sizes in the presence and absence of AMF. Inoculation with AMF increased DM production and nitrogen (N) yield of clover plants. Transfer of 15 N occurred between white clover and grass plants but was independent of AMF. Pore size of the mesh barriers controlled the degree of 15 N enrichment in the grass, suggesting that transfer was mediated by mass ¯ow and/or diusion. Additional experiments showed that grass roots could pass through pores of 60-lm diameter, and hyphal links could not be detected by autoradiography, thus supporting the conclusions of the tracer experiment. Ó 2000 Elsevier Science Ltd. All rights reserved. Keywords: Arbuscular mycorrhiza; Nitrogen transfer; White clover; Perennial ryegrass 1. Introduction Proposed routes for the transfer of nutrients, especially nitrogen (N), from legume to associated grass include death and decay of nodules and roots (Butler et al., 1959; Dubach and Russelle, 1994), exudation from legume roots (Ta et al., 1986) or by hyphal links formed by arbuscular mycorrhizal fungi (AMF) between legume and grass roots (Haystead et al., 1988). It is generally acknowledged that in grass/white clover associations turnover of N in roots, nodules and stolons is the major source of transferable N (Laidlaw et al., 1996) but the evidence for hyphae-mediated transfer of N between * Corresponding author. E-mail address: [email protected] (A. Scott Laidlaw). 1 Present Address. School of Environmental Management and Geography, University of the West of England, Frenchay Campus, Coldharbour Lane, Bristol BS16 1QY, UK. legumes and grass is con¯icting (Haystead et al., 1988; Barea et al., 1989; Frey and Sch uepp, 1993; Ikram et al., 1994). The strongest evidence for the positive role of N transfer by AMF from white clover to grass has been presented by Haystead et al. (1988) using a split root technique to label N in white clover. They compared the amount of N transferred to grass sharing the part of the clover root system fed from the remainder of the root system in an adjacent pot in the presence and absence of AMF. Roots in the shared pot were separated by barriers of mesh, the pore sizes of which were considered to allow solute diusion and mass ¯ow (3 lm), hyphae to pass through (60 lm), or the roots were completely separated by solid barriers or allowed to interact unhindered. Preliminary studies with mesh barriers of varying pore size indicated that 60 lm would allow roots to penetrate (Rogers, 1993) and so raised the possibility that the eect found by Haystead et al., may have been due to grass roots penetrating the mesh and exploring the N-rich rhizosphere in the clover compartment. 0045-6535/01/$ - see front matter Ó 2000 Elsevier Science Ltd. All rights reserved. PII: S 0 0 4 5 - 6 5 3 5 ( 0 0 ) 0 0 1 2 0 - X 154 J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 Rogers (1993) also found that a mesh with pore size of 5 lm was suciently small to prevent passage of external AMF hyphae. The present study was undertaken to investigate the eectiveness of barriers of varying mesh sizes in limiting N transfer and to re-evaluate the evidence regarding the role of AMF in forming eective hyphal links between perennial ryegrass and white clover. 2. Materials and methods 2.1. Experiment 1. The role of AMF in the transfer of nitrogen from white clover to perennial ryegrass The method of Haystead et al. (1988) outlined brie¯y above was followed with some modi®cations. In the split root assemblages, the barrier used to separate the root systems of the 15 N-fed donor and the receiver comprised nylon mesh of pore dimensions 5, 15 or 60 lm in addition to a complete barrier and no barrier. Inoculum comprised heavily mycorrhizal root fragments and adhering soil from grass/white clover plots in an experiment already described (Laidlaw et al., 1996). The inoculum was mixed thoroughly with the sterilised soil/sand mixture in the appropriate treatments and a pad of infected roots was also inserted below the roots of transplanted seedlings. Each assemblage consisted of two pots. All pots 15 15 cm2 were ®lled with three parts autoclaved acid-washed builderÕs sand: one part c-irradiated (1 Mrad) loam soil from the A horizon of a permanent pasture and the experiment comprised 60 assemblages. The experimental design was three replicated blocks of the ®ve barrier treatments with or without inoculum and with grass or clover as the `receiver'. One of the pots in each assemblage contained half of the root system of each pair of donor plants to which 15 N was applied, while the other contained the other half of the root system of the donor plants and that of the pair of receiver plants, separated from the donor roots unless barrierless. The mesh barriers were glued to 1-mm thick PVC frames, which in turn were axed to the pots with plastic cement and sealed with a self-curing non-toxic rubber sealant. The complete barrier was positioned with sealant only which was subsequently found to be inadequate and the eectiveness of the complete barrier broke down. Plants were grown in a slightly heated glasshouse (daytime maximum in the absence of sunlight was 15°C) and natural light was supplemented with mercury vapour lamps supplying 150±400 lmol mÿ2 sÿ1 for 12 h per day. 50 ml 25% full strength nutrient solution was applied weekly and 50 ml distilled water was applied daily to each pot containing roots of both species. Three weeks after setting up the experiment, 3.5 mg (15 NH4 )2 SO4 at 99.7 at.% excess was applied in solution every 2±3 days to the pot in each assemblage which contained half of the donor root systems. A total of 124 mg N per pot was supplied. 11 applications were made before the ®rst harvest, 16 between the ®rst and second harvests and 8 between the second and third. Donor and receiver plants were harvested to 2 cm above soil level 7, 12 and 18 weeks after planting. After 26 weeks donor shoots were harvested to ground level while receivers were harvested to 2 cm. Receiver shoots and roots were destructively sampled after a further four weeks. The proportion of length of roots infected with AMF was assessed in samples of roots of receiver plants which were cleared and stained at the end of the experiment using a modi®cation of the procedure of Phillips and Hayman (1970). The proportion was estimated using a grid-line intersection method from presence or absence of infection in roots at 200 intersections using 50 root segments per sample. Harvested herbage was dried at 60°C, milled and passed through a 280-lm sieve and analysed for total N and 15 N with a Europa Scienti®c ANCA/MS. 2.2. Experiment 2. To investigate the ability of grass and clover roots to penetrate mesh with pores of dierent diameters 14-day-old seedlings of white clover (cv Huia) and perennial ryegrass (cv Talbot), germinated on moist ®lter paper, were transplanted into 9-cm Petri dishes to provide a con®ned space to encourage penetration of the roots through the mesh of given pore size which lined the Petri dishes. Each dish had drainage holes on the base and was lined with a disc (diameter 11 cm) of 60, 35, 15 or 5 lm nylon mesh. The disc allowed the base and sides of the dish to be lined with a 2.5-mm lip around the top of the dish. The base of the dish was ®lled with a 1:1 (v/v) sand:soil mixture. The seedling was planted in the growth medium and the shoot was threaded through a hole of approximately 3-mm diameter cut in the centre of the lid of the dish. The lid was sealed to the base with insulating tape. 12 replicates were set up for each mesh size. The seedlings in the Petri dishes were arranged on plastic trays and placed in a growth cabinet at 20°C constant temperature set at a 16-h daylength and 90% humidity. 25 ml water and 10 ml of four-fold nutrient solution (Dart and Pate, 1959) were applied to the trays daily, ensuring that nutrients were always available within the Petri dishes. Six of the replicates were examined under a dissecting microscope for penetration of the mesh by seedling roots after ®ve weeks growth in the cabinet and the remaining six replicates were examined after a further four weeks. In instances where roots had penetrated, their length and diameter and presence or absence of branches was recorded. J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 2.3. Experiment 3. To investigate the possibility of transfer of carbon between roots of mycorrhizal perennial ryegrass and white clover using 14 C autoradiography Perennial ryegrass (cv Talbot) and white clover (cv Huia) seedlings were grown in a glasshouse (conditions similar to Experiment 1) in seed trays, grass for six weeks and clover for 8 weeks, in a sterilised sand:soil mixture either inoculated with AM fungi by mixing with colonised root fragments and AMF spores or uninoculated. Root washings were applied to the latter in an attempt to ensure microbial populations (other than mycorrhizal fungi) were similar in both media. 100-ml quarter strength nutrient solution was applied weekly and 100 ml distilled water twice weekly. After 6 weeks the grass and clover roots were 30±45% and 50±70% mycorrhizal, respectively. One clover and one grass plant, either mycorrhizal or non-mycorrhizal, were transplanted as a pair in factorial combination into specially adapted 9-cm diameter Petri dishes ®lled with sterilised sand comprising particles of 0.8±1.0 mm. Three holes of 5 mm diameter were drilled in the lid of each dish, one at one quarter along a diameter line, one in the centre and one three quarters along the same line. A plant was transplanted in the dish at the site of each of the two outer holes and water and nutrients were applied through the central hole. Each dish received 10 ml water twice weekly and 10 ml quarter strength nutrient solution once per week. After 4 weeks the lids of the dishes were sealed to the base with Terostat. Shoots of the clover plants were enclosed in a cellophane bag that had a 1-cm square rubber septum sealed on its surface. This allowed labelled salt solution and acid to generate 14 C to be introduced inside the bag into a 10 ml glass vial which had been placed on the lid of the Petri dish before the bag covered the clover shoots. 14 CO2 was generated by adding excess concentrated lactic acid to calcium carbonate Ca14 CO3 . This was calculated to expose the clover to 25 lCi of 14 CO2 . After 36 h of exposure, clover shoots were excised and the root systems prepared for autoradiography by washing soil from the roots in a ®ne jet of water but minimising disturbance by retaining the root system in the Petri dish. The root systems were photographed at 40 ´ magni®cation through the transparent dish base before being gently removed from the dish, blotted dry and placed on autoradiographic paper and sealed within a wooden cassette for 24 h. Photographs and autoradiographs were compared to identify the organs which had 14 C in the developed autoradiographic plates. 155 control and is not considered further. The 5-lm barrier is therefore taken as the treatment representing minimum rhizosphere interaction. Mean infection rate for roots of grass (based on root length infected) was 27.6% for inoculated and 0% for uninoculated treatments compared to 35.6% and 1.2% for corresponding infection rates for clover (Table 1). AMF inoculation had little eect on N content and DM yield of grass donor plants but signi®cantly increased N content and DM yield of white clover shoots from harvest 2 and 15 N enrichment of N in clover donor shoots was signi®cantly reduced due to AMF inoculation. Inoculation signi®cantly increased clover receiver shoot DM yield at three of the ®ve harvests but had no eect on grass receiver DM yield (data not presented). Nitrogen content of clover receiver shoots was signi®cantly increased by inoculation at harvests 2 and 4 but grass receiver shoots were unaected by inoculation. Inoculation did not aect 15 N enrichment of grass or clover receiver shoots (Table 2). Mean shoot DM yield of clover receiver plants was lower than grass shoots at the ®rst harvest but higher than grass at harvests 3, 4 and 5 (Table 3). Barrier type interacted with species at harvest 1 due to grass shoot DM being lower in the 5 lm mesh treatment than in the other treatments (except 15 lm), and at harvest 4 caused by DM yield of clover shoots being lower in the 60 lm treatments than the other barrier types. Clover receiver shoots had consistently higher N content than those of grass but N content was not aected by barrier type (Table 4). Except for harvest 1, clover receiver shoots had signi®cantly lower enrichment than grass receiver shoots. From harvest 3 onwards, enrichment of grass shoots was increased with increasing mesh pore size (Table 5). A mesh of pore size 35 lm allowed a few grass roots to penetrate, although the mean length of roots which breached the barriers was less than those which penetrated a 60 lm pore size (Table 6). With both of these mesh sizes, the mean width of the root at the other side Table 1 Experiment 1: percentage of root length of receiver plants colonised by AM fungi at the end of the experiment Barrier (lm) Inoculum Grass Clover Total + ) + ) + ) + ) + ) 30 0 27 0 33 0 22 0 26 0 42 2 38 1 32 0 43 3 23 0 5 15 3. Results 60 Due to the breakdown of the seams around the solid barrier, the `total barrier' treatment was an inadequate No barrier 156 J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 Table 2 Experiment 1: N content (g kgÿ1 ) and at.% excess in herbage in inoculation treatments (mean of barrier treatments) in receiver plant shoots Harvest Receiver Inoculum N content (g kgÿ1 ) 1 Clover + ) + ) 25.9 21.5 15.7 13.4 + ) + ) 39.5 35.6 15.3 14.3 + ) + ) 39.4 36.8 17.5 15.9 + ) + ) 34.2 28.0 12.7 12.0 + ) + ) 24.6 21.1 18.4 17.1 Grass 2 Clover Grass 3 Clover Grass 4 Clover Grass 5 Clover Grass SEM 1.91ns 1.91ns 0.98* 0.98ns 0.57ns 0.57ns 0.58* 0.58ns 0.99ns 0.99ns of the barrier from the plant was about twice that of the size of the pores. Clover roots were incapable of penetrating any of the barriers but root hairs were apparent at the other side of the barrier from the plant in barriers of 35 and 60 lm pore size. In Experiment 3, 14 C was detected in roots and shoots of white clover. Some roots of grass also contained 14 C. Although AMF hyphae could be seen, no hyphal links were apparent in the autoradiographs. at.% 15 N excess 2.49 3.88 1.85 1.41 SEM 0.35ns 0.35ns 0.07 0.11 0.21 0.50 0.11ns 0.11ns 0.11 0.08 0.70 0.55 0.09ns 0.09ns 0.02 0.03 1.01 0.82 0.08ns 0.08ns 0.11 0.14 1.18 1.38 0.05ns 0.05ns 4. Discussion Although mycorrhizal clover had a higher N yield and lower 15 N at.% excess enrichment than nonmycorrhizal clover, AMF infection did not appear to increase transfer of N from white clover to grass (or vice versa). The higher N yield and lower enrichment of mycorrhizal than non-mycorrhizal clover can be explained by AMF enhancing N2 -®xation (Hayman, Table 3 Experiment 1: DM yield (g potÿ1 ) of receiver shoots in each barrier treatment (mean of inoculation treatments) Species Barrier (lm) Harvest 2 3 4 5 Clover Total 5 15 60 None 328 358 420 368 505 273 610 468 392 448 281 387 471 269 469 415 777 840 497 622 757 1360 1258 1035 1310 Grass Total 5 15 60 None 1478 518 723 930 888 463 540 463 447 448 705 456 705 534 713 268 168 268 285 297 737 448 737 715 778 Species Barrier Species ´ Barrier SEM SEM SEM 1 36.0 57.0 80.6 49.2 77.8 110.0 1.57 2.48 3.51 31.7 50.1 70.9 54.1 85.5 120.9 J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 157 Table 4 Experiment 1: nitrogen concentration (g kgÿ1 ) in herbage in each barrier treatment (mean of inoculation treatments) in receiver plant shoots Species Barrier (lm) Harvest 1 2 3 4 5 Clover Total 5 15 60 None 22.2 24.4 24.8 23.5 23.7 37.4 39.9 37.9 34.7 38.0 37.3 38.0 38.9 36.9 39.4 33.4 31.1 30.3 28.5 31.9 23.8 23.1 24.4 21.5 21.7 Grass Total 5 15 60 None 15.1 13.7 15.9 13.2 14.8 14.6 15.7 14.6 14.0 14.7 16.2 17.2 16.2 16.6 16.7 12.3 12.5 12.3 12.7 11.9 18.4 18.0 18.4 18.5 17.3 Species Barrier Species ´ Barrier SEM SEM SEM Table 5 Experiment 1: at.% 15 0.94 1.49 2.10 0.50 0.79 1.11 0.49 0.78 1.10 0.45 0.71 1.01 0.57 0.90 1.27 N excess in herbage in each barrier treatment (mean of inoculation treatments) in receiver plant shoots Species Barrier (lm) Harvest 1 2 3 4 5 Clover Total 5 15 60 None 3.21 2.95 3.50 3.60 3.68 0.13 0.06 0.11 0.10 0.05 0.08 0.15 0.08 0.10 0.05 0.03 0.02 0.02 0.02 0.02 0.21 0.08 0.10 0.23 0.12 Grass Total 5 15 60 None 1.18 1.84 2.22 1.23 1.70 0.33 0.14 0.69 0.23 0.39 1.00 0.23 0.25 0.86 0.81 1.07 0.49 0.41 1.40 1.20 1.59 0.77 0.86 1.81 1.38 Species Barrier Species ´ Barrier SEM SEM SEM 0.320 0.506 0.716 0.084 0.133 0.189 0.060 0.095 0.134 0.056 0.088 0.125 0.040 0.063 0.089 1987). The higher infection rate of white clover roots than those of grass supports the proposition that clover roots are more mycotrophic than grass roots (Haynes, 1980). Taking the 5 lm barrier as a base on which to judge transfer of N in other treatments, about 30% more N was transferred in the 60 lm than the 5 lm treatment. However, this occurred irrespective of the presence of AMF. In the study of Haystead et al. (1988) in which they concluded that direct hyphal transfer of N between clover and grass occurred, a 60-lm mesh barrier was used to allow hyphae, but not roots, to pass. However, as found in Experiment 2 in this study, ®ne roots of grass can penetrate a 60-lm mesh. Hence it is possible that the greater amount of clover-derived N in grass separated from clover by the 60-lm mesh barrier in the mycorrhizal than the non-mycorrhizal treatment could have been due to more N being available to the ®ne roots of grass which had penetrated the barrier in the clover rhizosphere in the inoculated treatment. The absence of AMF-stimulated transfer in the 60 lm treatment in this study may have been due to the high N transfer in the non-mycorrhizal treatment masking any additional transfer which may have resulted from the greater root mass in the AMF treatment. Closeness of contact between the root systems of the legume and grass has been shown by Hamel et al. (1991) (working with soybean and maize) to be more important than AMF presence in N transfer. The nutrient status of the receiver relative to that of the donor has been considered to be a factor in determining the degree of hyphal mediated N transfer (Bethlenfalvay et al., 1991) although Frey and Sch uepp (1992) recorded some AMF-mediated N transfer 158 J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 Table 6 Experiment 2: details of penetration of pores in mesh barriers by roots of clover and grass Barrier (lm) Species Penetration of mesh 5 Clover Grass No No 0 0 0 0 0 0 15 Clover Grass No No 0 0 0 0 0 0 35 Clover Grass No Yes 0 2 0 230 0 84 60 Clover Grass No Yes 0 84 0 274 0 128 between berseem and maize even when maize was not apparently N-de®cient (Barber and Martin, 1976). As Experiment 1 progressed there was an indication that the smallest mesh size resulted in the lowest grass yield, suggesting that grass was relying on N from the clover donor. Despite that, and taking account of the fact that roots were well infected with AMF, mycorrhizal transfer was not apparent. Frey and Sch uepp (1992) have used a mesh of pore size 0.45 lm as a barrier to external hyphae of AMF. In this study it was considered that such a small pore size would be a hindrance to mass ¯ow and diusion as strong suction is required when using such membranes for ®ltration. Rogers (1993) found no evidence of external hyphae passing from inoculated roots through a membrane of 5 lm pore size when they were growing adjacent to the barrier. We are therefore convinced that the 5-lm pore size was an eective barrier for hyphae. 14 C was found in the grass roots in Experiment 3, suggesting that some form of transfer of carbon had occurred between the two root systems. It is well known that C is transported from shoots of AMF-infected plants into the hyphae, e.g. in cucumber plants (Jakobsen and Rosendahl, 1990). Although there was no indication from Experiment 3 of the root systems, by microscopy or from the autoradiographs that hyphal links had been involved in the transfer, it is possible that AMF external hyphae may have translocated 14 C from the donor plants and released it into the rhizosphere of the receivers. Alternatively, roots may have released carbon compounds during growth (Barber and Martin, 1976; Martin, 1977) and white clover roots turn over much faster than those of grass (Laidlaw et al., 1996). Therefore the 14 C in grass roots may have resulted from uptake of some of this released carbon. Further evidence against the implication of hyphal links in N transfer between clover and grass is the existence of partial ecological speci®city between AMF and their host, as has been found for AMF populations which infect white clover and perennial ryegrass (Rogers et al., 1994; Zhu et al., 2000). In conclusion, this study Mean root length Root diameter (lm) Prior to penetration After penetration suggests that N transfer between white clover and perennial ryegrass is unlikely to occur through AMF hyphal links in agricultural soils where the opportunities for alternative routes of transfer are likely to be well developed. Acknowledgements J.B. Rogers is grateful to the Ministry of Agriculture, Fisheries and Food for a postgraduate studentship. References Barber, D.A., Martin, J.K., 1976. The release of organic substances by cereal roots in soil. New Phytol. 76, 69±90. Barea, J.M., El-Atrach, F., Azcon, R., 1989. Mycorrhiza and phosphate interactions as aecting plant development, N2 ®xation, N-transfer and N-uptake from soil in legume-grass mixtures by using a 15 N dilution technique. Soil Biol. Biochem. 21, 581±589. Bethlenfalvay, G.J., Reye-Solis, M.G., Camel, S.K., FerreraCerrato, R., 1991. Nutrient transfer between soybean and maize connected by a common mycorrhizal mycelium. Physiol. Pl. 82, 423±432. Butler, G.W., Greenwood, R.M., Soper, K., 1959. Eects of shading and defoliation on the turnover of root and nodule tissue of plants of Trifolium repens, Trifolium pratense and Lotus uliginosus. N.Z. J. Agri. Res. 2, 415±426. Dart, P.J., Pate, J.S., 1959. Nodulation studies in legumes 3. The eects of delaying inoculation on the seedling symbiosis of barrel medic Medicago tribuloides. Desr. Austr. J. Biol. Sci. 12, 427±444. Dubach, M., Russelle, M.P., 1994. Forage legumes roots and nodules and their role in nitrogen transfer. Agron. J. 86, 259±266. Frey, B., Sch uepp, H., 1992. Transfer of symbiotically ®xed nitrogen from berseem (Trifolium alexandrinum L.) to maize via vesicular-arbuscular mycorrhizal hyphae. New Phytol. 122, 447±454. Frey, B., Sch uepp, H., 1993. A role of vesicular-arbuscular (VA) mycorrhizal fungi in facilitating interplant nitrogen transfer. Soil Biol. Biochem. 25, 651±658. J.B. Rogers et al. / Chemosphere 42 (2001) 153±159 Hamel, C., Barrentes-Cartin, U., Furlan, V., Smith, D.L., 1991. Endomycorrhizal fungi in nitrogen transfer from soybean to maize. Plant and Soil 138, 33±40. Haynes, R.J., 1980. Competitive aspects of the grass-legume association. Adv. Agron. 33, 227±261. Hayman, D.S., 1987. VA mycorrhizas in ®eld crop systems. In: Sa®r, G.R. (Ed.), Ecophysiology of VAM Plants. CRC Press, Boca Raton, pp. 172±192. Haystead, A., Malajczuk, N., Grove, T.S., 1988. Underground transfer of nitrogen between pasture plants infected with vesicular arbuscular mycorrhizal fungi. New Phytol. 108, 417±423. Ikram, A., Jensen, E.S., Jakobsen, I., 1994. No signi®cant transfer of N and P from Pueraria phaseoloides to Hevea brasiliensis via hyphal links of arbuscular mycorrhiza. Soil Biol. Biochem. 26, 1541±1547. Jakobsen, I., Rosendahl, L., 1990. Carbon ¯ow into soil and external hyphae from roots of mycorrhizal cucumber plants. New Phytol. 115, 77±83. Laidlaw, A.S., Christie, P., Lee, H.W., 1996. Eect of white clover cultivar on apparent transfer of nitrogen from clover 159 to grass and estimation of relative turnover rates of nitrogen in roots. Plant and Soil 179, 243±253. Martin, J.K., 1977. Factors in¯uencing the loss of organic carbon from wheat roots. Soil Biol. Biochem. 9, 1±7. Phillips, J.M., Hayman, D.S., 1970. Improved procedures for clearing roots and staining parasitic and vesicular-arbuscular mycorrhizal fungi for rapid assessment of infection. Trans. Br. Mycol. Soc. 55, pp. 158±160. Rogers, J.B., 1993. Investigation of the role of mycorrhizas in the transfer of nitrogen from white clover to grass. PhD Thesis, The QueenÕs University of Belfast, 216 pp. Rogers, J.B., Christie, P., Laidlaw, A.S., 1994. Some evidence for host speci®city in arbuscular mycorrhizas. Pedosphere 4, 377±381. Ta, T.C., McDowall, F.D.H., Faris, M.A., 1986. Excretion of assimilated N ®xed by nodules of alfalfa (Medicago sativa). Can. J. Bot. 64, 2063±2067. Zhu, Y.G., Laidlaw, A.S., Christie, P., Hammond, M.E.R., 2000. Ecological speci®city of arbuscular mycorrhiza fungi in perennial ryegrass-white clover pasture. Agriculture Ecosystems and Environment 77, 211±218.
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